Team:Imperial/Functionalisation
From 2014.igem.org
Functionalisation
Overview
(This overview is incomplete). By attaching functional proteins to cellulose we can expand it's properties and can bind specific contaminants in water. We used five different cellulose binding domains and fused them to different metal binding proteins, and sfGFP. We performed assays to test the binding of the CBD fusions to our cellulose.
Key Achievements
Introduction
![](https://static.igem.org/mediawiki/2014/a/a0/IC14-func-strategy-both-pursue.png)
Bacterial cellulose is already a useful biomaterial as is due its attractive mechanical properties, with research on applications from loudspeaker diaphragms to protective packaging and wound dressings (Lee 2014). However, our project also aims to extend the properties of cellulose by conjugating functional proteins and peptides to it. This allows us to target specific contaminants in water which can not be filtered by size exclusion alone. (See water report and informing design sections).
We considered two ways of functionalising cellulose (figure 1) but continued to work fully on the cellulose-binding domain (CBD) method. The curli-fibre method would be an exciting avenue to explore in the future; it is feasible since there has already been research into making a “programmable” biomaterial from curli fibres using a peptide tag approach (Nguyen et al 2014), and in combination with cellulose could produce a composite with robust mechanical properties as well.
Aims
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Cellulose Binding Domains (CBDs)
The cellulose binding domain (CBD) is the link between our functional proteins and the cellulose. Therefore, we wanted to use a CBD which had high affinity and strong binding to cellulose. However, weaker CBDs may still be useful since they could have the potential be controllably eluted under specific conditions, thereby enabling regeneration of the filter when saturated, and controlled disposal of the collected contaminants (refer to water report if relevant?).
We started our search by looking into the parts registry and found two CBDs already existed in the registry: CBDclos (BBa_K863111) and CBDcex (BBa_K863101). We also made three new CBDs to contribute to the registry: dCBD, CBDcipA, and CBDcenA. All the CBDs are in RFC(25) freiberg fusion format to allow for ease of use in protein fusions.
CBDclos and CBDcex
These parts were biobricked by Bielefeld 2012, please see their part pages (BBa_K863111a and BBa_K863101) for detailed information. CBDclos is from the cellulolytic bacterium Clostridium cellulovorans and CBDcex originates from the cellulolytic bacterium Cellulomonas fimi. This is the same organism as for CBDcenA; cex is from the exoglucanase gene and cen is from the endoglucanase gene.
Double CBD (dCBD) with N-terminal linker
This part, BBa_K1321340 is based on the double cellulose-binding domain construct synthesised and characterised by Linder et al1996, who found that this double CBD had higher affinity for cellulose than either of the two CBDs on their own. The main difference is that our part contains an additional linker sequence on the N-terminus of the protein.
The two CBDs are from the fungus Trichoderma reesei (Hypocrea jecorina) Exocellobiohydrolase (Exoglucanase) I (cbh1), uniprot ID P62694; and Exocellobiohydrolase (Exoglucanase) II, uniprot ID P07987 (cbh2); with a linker peptide between the two CBDs and at the N-terminus of the protein. Both linkers are the same amino acid sequence and are based on the endogenous linker sequences that exists in cbh1 and cbh2 genes. The linker sequence is PGANPPGTTTTSRPATTTGSSPGP which is the same as used by Linder et al 1996. The first three amino acids are from the cbh2 endogenous linker, and the rest is from the cbh1 endogenous linker. CBDcbh1 is placed C-terminal to CBDcbh2 because naturally CBDcbh1 is a C-terminal domain and CBDcbh2 is an N-terminal domain. Both CBDs are from the CBM family 1. The precise location of the CBD within the cbh genes was slightly different according to the uniprot annotations and the sequence used by Linder et al 1996; we chose to use the sequence from the paper since the protein was expressed and characterised successfully.
CBDcpiA with N and C-terminal linker
This CBD is from the Cellulosomal -scaffolding protein A (cipA) of Clostridium thermocellum including the endogenous linker sequences at the N and C-terminus (UniProt ID Q06851). It is in RFC25 format to allow for easy use in protein fusions.
The CBD is part of the CBM3 family . This CBD has been used in many application: in fusions with cell adhesion peptides to enhance the properties of cellulose as a cell-growth matrix (Andrade et al 2010a, Andrade et al 2010b), fused to enzymes to remove contaminants from water (Kauffmann et al 2000) and fused to an antimicrobial peptide (Ramos, Domingues & Gama 2010).
At present the cloning for these constructs is still in progress to correct an illegal EcoRI site which was identified in the parts with this CBD. This can be achieved with a silent mutation via site-directed mutagenesis and we aim to send these parts to the registry once thi
CBDcenA with C-terminal linker
This CBD is from the Endoglucanase A (cenA) gene from Cellulomonas fimi and also contains an endogenous C-terminal linker. The cellulose binding domain region occurs at the N-terminus of the cenA gene (UniProt P07984 link to http://www.uniprot.org/uniprot/P07984) and is from the CBM family 2
The linker sequence (PTTSPTPTPTPTTPTPTPTPTPTPTPTVTP) is Pro-Thr box which has an extended conformation and acts as a hinge region (Gilkes et al 1989). The endoglucanase CBDcenA has 50% homology to the exoglucanase CBDcex (BBa_K863101) and the linker is highly conserved in both, but the order of the catalytic, linker and cellulose-binding regions is reversed (Warren et al 1986). It has been shown that CBDcenA has the highest binding affinity for crystalline cellulose out of the C. fimi CBDs (Kim et al 2013).
Functionalisation proteins: Binding partners
Superfolder Green Fluorescent Protein (sfGFP)
Metal Binding Proteins
One of the contaminants we can filter out which current size-exclusion technologies can not target, are heavy metals. We have worked with four different metal binding proteins: the metallothioneins SmtA and fMT, a histidine-rich nickel binding protein (NiBP) from the bacterium Heliobacter pylori and a synthetic phytochelatin (PC) EC20.
SmtA and fMT metallothioneins
These two parts already existed in the BioBrick registry, but since we needed to use them as fusions with the CBDs we improved the parts by making them compatible with the RFC(25) Frieburg Fusion BioBrick standard.
Metallothioneins (MTs) are genetically encoded cysteine-rich peptides which serve a role in the detoxification of heavy metals in plants, animals and some prokaryotes (Cobbett, 2002). They have a similar structure and function to phytochelatins, but are produced by different mechanisms (Cobbett, 2002). SmtA is from the cyanobacteria Synechococcus sp. and was used by the Tokyo-NoKoGen 2011 iGEM team (who submitted the RFC10 part originally, BBa_K519010) to confer cadmium (Cd2+) tolerance to E. coli cells when expressed. fMT originates from the seaweed Fucus vesiculosus and was submitted by Groningen 2009 iGEM team and detailed information can be found on the original part page (BBa_K190019).
We successfully cloned the following CBD fusion constructs:
Nickel binding protein (NiBP)
We successfully cloned the following CBD fusion constructs with NiBP:
However we discovered late on in the project that the DNA sequence of the NiBP protein in the registry is out of frame, leading to an incorrect protein translation and read-through of the stop codon (figure 2).
Further investigation into the error let us to identify a single nucleotide deletion in BBa_K1151001 compared to the native H.pylori DNA sequence (GenBank CP000012.1 bp1391851-1392033, reverse complement strand).
Synthetic phytochelatin EC20
This is our new contribution of a metal-binding protein to the parts registry. Synthetic phytochelatins are analogues of phytochelatins (PCs); cysteine-rich peptides of the general structure (γ-GluCys)n-Gly (n~2-5) which bind and sequester heavy metals, with a role in detoxification (Cobbett & Goldsbrough 2002). PCs are found mainly in plants but also in other organisms including diatoms, fungi, algae (including cyanobacteria) and some invertebrates (Cobbett & Goldsbrough 2002, Rea 2012). Natively, the PCs are enzymatically synthesized by phytochelatin synthase (PCS) from a glutathione (GSH) precursor and the amino acids in the resulting peptide are linked by the non-standard gamma peptide bonds (Cobbett & Goldsbrough 2002, Rea 2012). However, genetically encoded analogues (containing normal alpha-peptide bonds) of different number Glu-Cys (EC) repeats have been characterised, with the EC20 having the highest binding (Bae et al 2000).
The main metal PCs confer tolerance to is Cadmium (Cobbett & Goldsbrough 2002) with a reported stoichiometry of 10 Cd2+ per peptide (Bae et al, . EC20 peptide has still showed good metal ion binding whilst fused to a cellulose binding domain (CBD) for water purification (Xu et al 2002) and when anchored to bacterial cell membrane to confer Cd2+ tolerance (Bae et al 2000, Chaturvedi & Archana 2014). PC EC20 has also been shown to bind many more heavy metals. For example, when displayed on the surface of Cupriavidus metallidurans, the cells capacity to adsorb ions increased by 31 to 219% depending on the ion (table 1, Biondo et al 2012). These binding properties of PC EC20 have been utilised in applications including a regeneratable biosensor of Hg2+, Cd2+, Pb2+, Cu2+ and Zn2+ ions to 100 fM–10 mM (Bontidean et al 2003), and to target CdSe/ZnS quantum dots to streptavidin expressing HeLa cells when biotinylated (Pinaud et al 2004). INSERT TABLE OF THE IONS FROM THE PAPER
We used this part to clone a library of different cellulose-binding domains fused to phytochelatin:
Other potential proteins
During our research we also explored other functional proteins to fuse to the CBDs.
Laccases
Laccases are enzymes which can break down aromatic and phenolic compounds such as modified estrogens which can end up unfiltered in the water supply with unknown consequences (Auriol et al 2008). This method of treating estrogen in water was explored by Bielefeld 2012 iGEM team, and our system also has potential to address this.
Nanobodies
Nanobodies are fragments of camelid antibodies which can be generated against a variety of antigens and can be easily expressed by organisms such as E. coli . Nanobodies could be used to target viruses, which are often too small to be filtered by size exclusion. For example there are already nanobodies which can bind to Vaccinia virus, ricin, Cholera toxin, Stephylococcal enterotoxin B and H5N1 Influenza (Goldman et al 2006, Ibanez et al 2011) to name a few. Additionally, nanobodies are stable and can be selected to resist proteolytic attach (Harmsen et al 2006). Nanobodies can also be functional when as fusions or conjugates to other proteins for example to target enzymes to specific cells (Cortez-Retamozo 2004), so there is much potential for targeting a wide array of contaminants when fused to cellulose binding domains.
Results
Lorem ipsum dolor sit amet, consectetuer adipiscing elit. Aenean commodo ligula eget dolor. Aenean massa. Cum sociis natoque penatibus et magnis dis parturient montes, nascetur ridiculus mus. Donec quam felis, ultricies nec, pellentesque eu, pretium quis, sem. Nulla consequat massa quis enim. Donec pede justo, fringilla vel, aliquet nec, vulputate eget, arcu. In enim justo, rhoncus ut, imperdiet a, venenatis vitae, justo. Nullam dictum felis eu pede mollis pretium. Integer tincidunt. Cras dapibus. Vivamus elementum semper nisi. Aenean vulputate eleifend tellus. Aenean leo ligula, porttitor eu, consequat vitae, eleifend ac, enim.
References
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- Bontidean, I., Ahlqvist, J., Mulchandani, A., Chen, W., et al. (2003) Novel synthetic phytochelatin-based capacitive biosensor for heavy metal ion detection. Biosensors and Bioelectronics. 18 (5-6), 547–553.
- Lee, K.-Y., Buldum, G., Mantalaris, A. and Bismarck, A. (2014), More Than Meets the Eye in Bacterial Cellulose: Biosynthesis, Bioprocessing, and Applications in Advanced Fiber Composites. Macromol. Biosci., 14: 10–32. doi: 10.1002/mabi.201300298
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- Linder, M.; Salovuori, I.; Ruohonen, L.; Teeri, T.T., 1996. Characterization of a Double Cellulose-binding Domain. SYNERGISTIC HIGH AFFINITY BINDING TO CRYSTALLINE CELLULOSE. Journal of Biological Chemistry, 271(35), pp.21268–21272. Available at: http://www.jbc.org/content/271/35/21268.full
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